CA3046063A1 - Methods of pulp fiber treatment - Google Patents

Methods of pulp fiber treatment Download PDF

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CA3046063A1
CA3046063A1 CA3046063A CA3046063A CA3046063A1 CA 3046063 A1 CA3046063 A1 CA 3046063A1 CA 3046063 A CA3046063 A CA 3046063A CA 3046063 A CA3046063 A CA 3046063A CA 3046063 A1 CA3046063 A1 CA 3046063A1
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pulp
bleaching
singlet oxygen
peracetate
stage
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Wayne E. Buschmann
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Clean Chemistry Inc
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Clean Chemistry Inc
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12PFERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
    • C12P3/00Preparation of elements or inorganic compounds except carbon dioxide
    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C9/00After-treatment of cellulose pulp, e.g. of wood pulp, or cotton linters ; Treatment of dilute or dewatered pulp or process improvement taking place after obtaining the raw cellulosic material and not provided for elsewhere
    • D21C9/10Bleaching ; Apparatus therefor
    • D21C9/1063Bleaching ; Apparatus therefor with compounds not otherwise provided for, e.g. activated gases
    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C9/00After-treatment of cellulose pulp, e.g. of wood pulp, or cotton linters ; Treatment of dilute or dewatered pulp or process improvement taking place after obtaining the raw cellulosic material and not provided for elsewhere
    • D21C9/10Bleaching ; Apparatus therefor
    • D21C9/147Bleaching ; Apparatus therefor with oxygen or its allotropic modifications
    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C9/00After-treatment of cellulose pulp, e.g. of wood pulp, or cotton linters ; Treatment of dilute or dewatered pulp or process improvement taking place after obtaining the raw cellulosic material and not provided for elsewhere
    • D21C9/10Bleaching ; Apparatus therefor
    • D21C9/16Bleaching ; Apparatus therefor with per compounds
    • D21C9/166Bleaching ; Apparatus therefor with per compounds with peracids
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/008Control or steering systems not provided for elsewhere in subclass C02F
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/76Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/76Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
    • C02F1/766Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens by means of halogens other than chlorine or of halogenated compounds containing halogen other than chlorine
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/02Non-contaminated water, e.g. for industrial water supply
    • C02F2103/023Water in cooling circuits
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/26Nature of the water, waste water, sewage or sludge to be treated from the processing of plants or parts thereof
    • C02F2103/28Nature of the water, waste water, sewage or sludge to be treated from the processing of plants or parts thereof from the paper or cellulose industry
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/32Nature of the water, waste water, sewage or sludge to be treated from the food or foodstuff industry, e.g. brewery waste waters
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/04Oxidation reduction potential [ORP]
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/36Biological material, e.g. enzymes or ATP
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/02Odour removal or prevention of malodour
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/08Corrosion inhibition
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/20Prevention of biofouling

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Wood Science & Technology (AREA)
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Abstract

In some embodiments, a method may include treating pulp. The method may include contacting a wood pulp with a singlet oxygen source. The method may include contacting the wood pulp with an alkaline peroxide source. The singlet oxygen source may include a peracetate oxidant solution and generating a reactive oxygen species. The peracetate oxidant solution may include peracetate anions and a peracid. In some embodiments, the peracetate solution may include a pH from about pH 10 to about pH 12. In some embodiments, the peracetate solution has a molar ratio of peracetate anions to peracid ranging from about 60: 1 to about 6000: 1. In some embodiments, the peracetate solution has a molar ratio of peracetate to hydrogen peroxide of greater than about 16:1. The peracetate oxidant solution may provide enhanced treatment methods of bleaching, brightening, and delignifying pulp fibers involving the use of peracetate oxidant solutions.

Description

TITLE: METHODS OF PULP FIBER TREATMENT
BACKGROUND OF THE INVENTION
1. Field of the Invention [0001] The present disclosure generally relates to pulp fiber treatment using peracetate oxidant solutions. The disclosure more particularly relates to methods of bleaching, brightening, and delignifying pulp fibers involving the use of peracetate oxidant solutions to provide singlet oxygen.
2. Description of the Relevant Art [0002] A variety of methods have been developed for delignification of wood pulp fibers after the initial pulping to achieve brighter unbleached grades and bleachable grades (e.g., kappa number 10-15). Common delignification methods include reductive methods (e.g., extended or enhanced sulfide digestion), oxidative methods (e.g., oxygen delignification, alkaline hydrogen peroxide extraction and combinations), and enzymatic methods (e.g., zylanase).
[0003] Bleaching of pulp (wood and non-wood fibers) is commonly done by elemental chlorine free (ECF) processes and totally chlorine free (TCF) processes. The ECF
processes are currently more economic and common than TCF in large pulp and paper mills for reaching white fiber grades of greater than about 80% ISO brightness. ECF bleaching commonly involves several chlorine dioxide stages with washing and extraction stages in between. TCF
processes may incorporate extended delignification stages and alternative bleaching chemicals including multiple alkaline hydrogen peroxide stages, ozone and peracetic acid to achieve brighter fiber grades.
[0004]
Singlet oxygen is well suited for oxidation of phenols, chlorinated phenols and similar electron-rich phenolic materials including lignin. Lignin generally consists of crosslinked polyphenolic materials created by enzyme-mediated polymerization of coniferyl, sinapyl and p-coumaryl alcohols. Singlet oxygen (which is not a radical) is relatively selective towards phenol oxidation and has little direct impact on cellulose fibers. In contrast, ozone and radicals including elemental chlorine, hydroxyl radical, hydroperoxyl radical, superoxide and even triplet oxygen are more reactive towards cellulose in conventional delignification and bleaching processes.
[0005]
The selectivity of singlet oxygen towards the oxidation and break down of lignin and non-cellulose materials avoids non-selective reactions that break down cellulose by radical-based or radical-forming oxidants including gaseous chlorine, chlorine dioxide and ozone. Reactive oxygen radical species such as superoxide and peroxyl radicals are known to form during higher pressure and temperature oxygen delignification processes and can cause damage to cellulose fibers. It is generally known in the art that cellulose fibers are susceptible to damage by radical species, which reduces fiber yield and fiber strength. The addition of alkali to oxygen delignification and hydrogen peroxide extraction is common practice to increase the oxidation and extraction rates of lignin from cellulose fiber. However, excessive alkali concentrations or exposure times will also cause damage to cellulose fiber.
[0006]
The rate of delignification also impacts the preservation of pulp fiber yield, strength and quality. Shorter exposure time of fiber to oxidizing and alkaline conditions may reduce the amount of non-selective breakdown of cellulose fiber. For example, an oxygen delignification process for wood pulp is typically 30 to 60 minutes retention time to achieve about 20-60% kappa reduction depending on the oxygen stage design, operating conditions and wood species. In comparison, the use of the peracetate oxidant formulation may achieve the same kappa reduction performance in 1 to 20 minutes contact time or retention time depending on the wood species, process design and operating conditions. Shorter retention times may also increase pulp throughput or decrease the size and cost of equipment for a delignification process.
[0007] Studies of singlet oxygen oxidation of phenols has historically been conducted using photocatalytic methods to generate singlet oxygen in-situ. This method often involves irradiation of a solution containing a photosensitive dye (e.g., rose bengal, methylene blue) which transfers its photo-excited state energy to dissolved oxygen. Relying on a dye mediated photooxidation process is not practical for pulp delignification due to optically opaque pulp mixtures and the rapid breakdown of photosensitive dyes by singlet oxygen and other ROS.
[0008]
Polychlorinated phenols are one of the major absorbable organic halogens (AOX) that may be discharged in pulp bleaching effluents. Dioxins, furans and other halogenated organic materials are also formed during chlorine and chlorine dioxide bleaching and are included in the AOX category. AOX formation is highly dependent on the lignin content (proportional to kappa number) of the pulp prior to bleaching. The more reduction in kappa number prior to bleaching the less AOX formation potential. The ROS-generating peracetate formulation has the ability to reduce kappa number (lignin content) significantly.
[0009]
Furthermore, there are few economically viable options for delignification and bleaching of wood and non-wood pulps on smaller scales than those feasible for traditional pulp and kraft pulp mills. Oxygen delignification has very high capital costs and significant operating and maintenance costs. Digesters for reductive, hydrolytic and enzymatic methods have moderate capital costs but may occupy a large footprint and have long retention times.
Adding new bleaching plants to existing facilities is often not economically feasible, especially for smaller capacity facilities (e.g., less than 1000 tons per day product). Options for delignification and bleaching which are lower cost and simpler to implement or retro-fit into a pulp treatment process will be beneficial to smaller and existing fiber lines.
[0010]
Fiber products, including fiber board and molded fiber products, produced from pulps of various types used in food packaging and compostables are generally unbleached if gaseous chlorine, chlorine bleach and chlorine dioxide are excluded from the processing. Producing these products with brightened (e.g., 65% ISO brightness or greater) or near-white grades of fiber without the use of traditional bleaching lines is desirable.
[0011]
The use of elevated concentrations of chlorine dioxide in water treatment is particularly hazardous. For example, the head space of a tank containing water with 20 mg/L
chlorine dioxide will slowly equilibrate to a head space concentration of 807 mg/m3 at 25 C
and 1 atm according to Henry's law calculations. Pulp bleaching operations using chlorine dioxide at several hundred to several thousand mg/L concentrations and elevated temperatures pose severe exposure hazards over large areas if not properly contained. Gases are more difficult to contain than liquid solutions with low vapor pressures. Chlorine dioxide is also an explosive gas and can undergo explosive decomposition above 10% v/v chlorine dioxide in air. Above 14% explosions are violent.
Explosive vapor concentrations can be achieved in pipes that are only partially filled with moderately concentrated chlorine dioxide solutions.
[0012]
Water used in chlorine and chlorine dioxide bleaching stages is not compatible with recovery boilers and other process equipment outside of the bleaching circuit due to the highly corrosive chloride and chlorate content. Chlorides would accumulate in closed loop processes in a pulp mill used upstream of the bleaching circuit causing corrosion damage to conventional process equipment. Therefore, the water from bleaching stages, which also contains the majority of AOX emissions, must be segregated, treated and disposed of as waste water.
The peracetate oxidant formulation contains no chloride content and its organic carbon content can be combusted in the recovery boilers. Each chlorine or chlorine dioxide bleaching stage that is replaced or reduced by using the peracetate oxidant formulation upstream of the bleaching circuit represents a reduction in the waste water stream, reduction in AOX and reduced financial and environmental costs of treatment and disposal or discharge.
[0013]
Corrosivity of radical compounds used in the delignification, brightening and bleaching stages is another issue, especially when these compounds come in contact with various process materials such as steel, copper and brass alloys. These compounds used in processes where elevated temperatures and turbulence are present in the liquid phase should ideally have low vapor pressures to minimize vapor phase corrosion of surrounding equipment and structures.

Compounds that are gases in their native form are the most volatile and present the greatest corrosion and occupational exposure hazards, including chlorine, chlorine dioxide and ozone.
[0014] There is a need for improved oxidation and extraction of colored materials and color-forming materials from pulp fibers for brightening and bleaching purposes. It is desirable to find an efficient and cost effective method of treating pulp without the use of halogen-containing bleaching chemicals. It is also desirable to conduct bleaching of pulp by new methods to achieve the desired brightness which are less damaging to pulp fiber and extract less mass of pulp during bleaching to increase pulp yield relative to conventional pulp bleaching methods. The reactive oxygen species (ROS) generating peracetate formulation of the present invention may be used for decreasing the use of halogen-containing oxidants and thus TOX and AOX
formation. Use of the peracetate formulation in pulp processing may reduce pollution, reduce waste water effluent and enhance processes for extracting lignin from cellulosic fiber for the recovery of lignin from the black liquor or spent oxidant liquor.
SUMMARY
[0015] In some embodiments, methods described herein may use ROS
formulations, which generate singlet oxygen as the primary ROS, in bleaching sequences to brighten and whiten pulp fiber such that chlorine and chlorine dioxide use may be significantly reduced to increase pulp yield and preserve fiber strength.
[0016] In some embodiments, methods described herein using ROS
formulations in bleaching sequences enable the brightening and whitening of pulp without removing as much material from pulp as conventional ECF bleaching sequences (e.g. DEDD bleach sequence).
[0017] In an embodiment, the methods described herein provide a method of bleaching pulp using a singlet oxygen stage followed by an alkaline peroxide stage. Peroxide may be in the form of hydrogen peroxide, sodium peroxide, potassium peroxide or calcium peroxide.
Peroxide may be in the form of a percarbonate, a perborate or a persulfate.
[0018] In an embodiment, the methods described herein provide a method of bleaching pulp using a singlet oxygen stage followed by an alkaline peroxide stage at least once during a bleach sequence. The alkaline hydrogen peroxide stage removes the remaining lignin and other materials impacted by the singlet oxygen stage, but not extracted into the singlet oxygen liquor. Without an alkaline peroxide stage for extraction after a singlet oxygen stage the oxidant demand for a subsequent chlorine dioxide stage is not significantly reduced.
[0019]
Singlet oxygen can rapidly oxidize and extract lignin and non-lignin colored materials from pulp while making residual materials that remain in the pulp more readily extractable in subsequent bleaching stages. Residual materials may be bound or unbound to pulp fiber structures including hemicellulose structures and cellulose structures. Subsequent bleaching stages may .. include alkaline hydrogen peroxide, chlorine dioxide, ozone and peracetic acid. In one embodiment, a singlet oxygen stage, 10, is followed by an alkaline hydrogen peroxide stage, P, to significantly increase brightness and reduce the amount of C102 required in an ECF bleaching sequence. A chelating wash stage, Q, may be used just prior to an alkaline hydrogen peroxide stage, but after the 10 stage.
A chelating agent used in Q stage may include ethylenediaminetetraacetic acid (EDTA) and diethylenetriaminepentaacetic acid (DTPA). An alkaline hydrogen peroxide stage may include the use of a magnesium salt such as magnesium sulfate. An alkaline hydrogen peroxide stage may be followed by a singlet oxygen stage. A
chlorine dioxide stage, D, may be conducted after an alkaline hydrogen peroxide stage. A chlorine dioxide stage may be followed by subsequent chlorine dioxide, peracetic acid, Paa, alkaline .. extraction, E, and/or alkaline hydrogen peroxide stages. An ozone stage, Z, may be used before or after any such stages listed above.
[0020]
In one embodiment a bleaching sequence is 10 P, which may be followed by additional bleaching stages. In other embodiments the bleaching sequence may be chosen from the following examples (these examples are not meant to be limiting):
10 P;
10 Q P;
lop 10 P;
1013Z E;
10P DP;
10 QPDP;
10 Q P 10 P;
10 PD D;
10PDPD;
10PDED;
10 P 10 P D P;
10 P Paa P D P;
10P D Paa P;
lOPZEDP;
Z E 10 P; and ZE 10PDP.
[0021] A first singlet oxygen stage may be conducted after a pulping process including mechanical, chemical, sulfide digestion, steam explosion and enzymatic pulping processes or a combination of pulping processes. A first singlet oxygen stage may be conducted after a delignification stage including oxygen delignification and peroxide-reinforced oxygen delignification.
[0022] In a preferred embodiment a bleaching sequence may be singlet oxygen, followed by chelation, followed by alkaline hydrogen peroxide, where the bleaching sequence is represented as 10 Q P. This bleaching sequence may achieve pulp brightness of 60% ISO or greater without further bleaching steps.
[0023] In a preferred embodiment a bleaching sequence may be singlet oxygen, followed by chelation, followed by alkaline hydrogen peroxide, followed by chlorine dioxide, followed by alkaline hydrogen peroxide, where the bleaching sequence is represented as 10 Q P D P. This bleaching sequence may achieve pulp brightness of 80% ISO or greater without further bleaching steps. This bleaching sequence may preferably achieve pulp brightness of 85%
ISO or greater without further bleaching steps.
[0024] In another embodiment a bleaching sequence may be singlet oxygen, followed by chelation, followed by alkaline hydrogen peroxide, followed by singlet oxygen, followed by alkaline hydrogen peroxide, where the bleaching sequence is represented as 10 Q P 10 P. This bleaching sequence may achieve pulp brightness of 60% ISO or greater, 70% ISO
or greater, or 80% ISO or greater without further bleaching steps. This bleaching sequence may preferably achieve pulp brightness of 85% ISO or greater without further bleaching steps.
[0025] In an embodiment, a method may include rapidly optimizing a bleach sequence by monitoring and/or evaluating absorbance spectra of bleaching liquors, fiber brightness and/or fiber viscosity. Evaluating the amount and type of materials extracted during a bleach sequence or individual stages within the sequence is rapidly conducted by measuring the UV-Vis absorbance spectrum of bleaching liquors. The amount of lignin and other oxidizable materials removed from or remaining in pulp can be rapidly evaluated with kappa number measurements.
The impact of a bleach sequence or individual stages within the sequence on fiber brightening may be rapidly evaluated and quantified by brightness measurements. The impact of a bleach sequence or individual stages within the sequence on chemical impacts on the cellulose structure of the pulp fiber may be rapidly evaluated and quantified by viscosity measurements. A
combination of these analysis methods provides a method for preliminary evaluation of bleach sequence conditions.
[0026] In an embodiment, a method of using a singlet oxygen stage followed by an alkaline peroxide stage to achieve a pulp brightness of about 60% ISO or greater.
[0027] In an embodiment, a method of using a singlet oxygen stage followed by an alkaline peroxide stage to reduce the amount of chlorine dioxide used in a bleach sequence by up to about 97% to achieve a pulp brightness of about 60% ISO or greater.
[0028] In an embodiment, a method of using a singlet oxygen stage followed by an alkaline peroxide stage to reduce the amount of chlorine dioxide used in a bleach sequence by up to about 95% to achieve a pulp brightness of about 80% ISO or greater.
[0029] In an embodiment, a method of using more than one pair of singlet oxygen and alkaline hydrogen peroxide stages in a bleach sequence to achieve a pulp brightness of about 60% ISO or greater. It was found that using two or more singlet oxygen stages paired with alkaline peroxide stages used sequentially could provide significant brightness gains without the use of chlorine dioxide.
[0030] In an embodiment, the use of singlet oxygen and alkaline hydrogen peroxide stages together can provide a new method for totally chlorine free (TCF) bleaching of pulp. In an embodiment, a preferred method may include a singlet oxygen stage followed by a chelating wash stage followed by an alkaline peroxide stage may achieve pulp brightness of about 60% ISO or greater. This bleaching sequence may preferably achieve pulp brightness of 70%
ISO or greater without further bleaching steps.
[0031] In an embodiment, a method of using more than one pair of singlet oxygen and alkaline hydrogen peroxide stages in a bleach sequence to achieve a pulp brightness of about 80% ISO or greater. This bleaching sequence may preferably achieve pulp brightness of 85%
ISO or greater without further bleaching steps.
[0032] In an embodiment, the method of using at least one singlet oxygen stage in a bleach plant wherein a singlet oxygen stage and an alkaline peroxide stage are used in a bleach plant.
[0033] In an embodiment, the method of using at least one singlet oxygen stage in a pulp plant wherein a singlet oxygen stage and an alkaline peroxide stage are used in a pulp plant.
[0034] The sodium peracetate formulation comprising the ROS formulation is chlorine-free and its byproducts in pulp liquors are compatible with recovery boilers for closed-loop recycle processes. A bleach sequence using at least one singlet oxygen stage may be conducted fully within a bleach plant. A bleach sequence using at least one singlet oxygen stage may be conducted partly in a pulp plant where the bleach stages prior to a chlorine dioxide or chlorine stage are compatible with a pulp plant process. A bleach sequence using at least one singlet oxygen stage may be conducted fully in a pulp plant where chlorine dioxide and chlorine are not used in a bleach sequence.
[0035] In an embodiment, a method of using at least one singlet oxygen stage to reduce bleach plant water consumption. Reducing the amount of chlorine dioxide or chlorine used and the number of steps in which they are used in a bleach sequence reduces the amount of water used in a bleach plant. This reduces the amount of water used in the chlorine dioxide or chlorine treatment steps and reduces the amount of water used to wash the pulp after chlorine dioxide or chlorine steps.
[0036] In an embodiment, a method may include using at least one singlet oxygen stage to reduce the quantity of bleach plant water effluent. Reducing bleach plant water consumption reduces the amount of effluent from a bleach plant that requires treatment or disposal. Bleach plant water effluent is not compatible with recovery boilers for closed-loop recycle processes.
[0037] In an embodiment, a method of using singlet oxygen in a bleach sequence to preserve pulp fiber viscosity. Singlet oxygen provided by the ROS formulation does not have a significant negative impact on the pulp fiber's cellulosic structure. Under natural pH or pulp pH conditions in a mill fiber line (e.g., pH 6.0-10.8) the singlet oxygen ROS formulation can have little to no impact on pulp viscosity in a bleach sequence. A result of dramatically reducing C102 use in a bleach sequence is that it has greatly reduced or minimal impact on viscosity.
Therefore, a combination of singlet oxygen and low C102 use can better preserve the viscosity of pulp fiber, which results in higher strength fiber after bleaching.
[0038] In an embodiment, a method of using singlet oxygen in a bleach sequence to increase pulp yield. Using singlet oxygen provided by a ROS formulation in a bleach sequence increased pulp brightness with significantly less corresponding reduction in kappa number than conventionally bleached pulps (e.g., ECF bleach sequences that achieve brightness of 70% ISO or greater). Pulp yield has been correlated with kappa number in the pulp industry (for example see L.D. Shackford, "A Comparison of Pulping and Bleaching of Kraft Softwood and Eucalyptus Pulps," 36th International Pulp and Paper Congress and Exhibition; October 13-16, 2003, Sao Paulo, Brazil, incorporated by reference herein) and the correlation is generally consistent for each wood species. For example, hardwood species like spruce and birch bleached to a brightness of 85% ISO typically have a kappa number of about 1, a common "market pulp"
grade. It was demonstrated using methods described herein that incorporating a singlet oxygen stage in a hardwood pulp bleach sequence could provide a final brightness of 85% ISO with a kappa number of about 4.4.
[0039]
Increasing the amount of singlet oxygen used in the bleaching sequence was found to increase the final kappa number of the pulp after the entire bleaching sequence. The singlet oxygen chemistry provided by the ROS formulation modifies the pulp in a manner that serves to protect non-colored materials in the pulp from oxidation and extraction in subsequent bleaching stages.
[0040] Types of fiber treated in this invention include wood pulp and other fibers used in paper, packaging and molded fiber products including bamboo, eucalyptus, wheat straw, rice, bagasse, palm, flax and other plant-based sources. The lignocellulosic pulp employed in the present invention can be prepared from any lignocellulose-containing material derived from natural sources such as, but not limited to, hardwood, softwood, gum, straw, bagasse and/or bamboo by various chemical, semichemical, thermal, mechanical or combination pulping processes. Chemical and semichemical pulping processes include, but not limited to kraft, modified kraft, kraft with addition of sulfur and/or anthraquinone, and sulfite. Mechanical pulping processes include, but not limited to stone groundwood, pressurized groundwood, refiner mechanical, thermo-refiner mechanical, pressure refined mechanical, thermo-mechanical, pressure/pressure thermo- mechanical, chemi-refiner-mechanical, chemi-thermo-mechanical, thermo-chemi-mechanical, thermo-mechanical-chemi, and long fiber chemi-mechanical pulp.
Handbook for Pulp and Paper Technologist, ed. G. A. Smook (Atlanta, GA, TAPPI
Press, 1989) describes both chemical and mechanical pulping.
[0041]
In some embodiments, the correlations between kappa number and brightness have been disrupted. The current methods preserve pulp viscosity (a strength parameter).
The current methods reduce C102 use dramatically and quantifiably. The current methods reinforce or enhance C102 performance (measurable by UV). In some embodiments, some or all of this may be accomplished by designing bleach sequences. Previous methods did not include alkaline peroxide step (previous methods only replaced peroxide with singlet oxygen compositions in a C102 bleach sequence).
BRIEF DESCRIPTION OF THE DRAWINGS
[0042]
Advantages of the present invention may become apparent to those skilled in the art with the benefit of the following detailed description of the preferred embodiments and upon reference to the accompanying drawings.
[0043]
FIG. 1 depicts examples of UV-Vis absorption spectra of alkaline hydrogen peroxide liquors from hardwood (upper trace) and softwood (lower trace) pulps.
[0044]
FIG. 2 depicts pulp brightness of the initial oxygen delignified hardwood, 0, and after each stage of the bleach sequence 10 P D P.
[0045] FIG. 3 depicts fiber viscosity of the initial oxygen delignified hardwood, 0, and after each stage of the bleach sequence 10 P D P.
[0046] FIG. 4 depicts ISO brightness versus kappa number of hardwood samples analyzed at various points before, during and after the bleach sequences 10 P D P and 10 QPDP (solid circles). A bleached market pulp control sample was also analyzed (open square).
[0047] FIG. 5 depicts the relative absorbance of the 280 nm (circles), 350 nm (squares) and 420 nm (triangles) points in the hardwood UV-Vis absorbance spectra of the D
stage liquors versus the 10 stage peracetate concentration. The dashed lines are provided to help guide the eye.
[0048] FIG. 6 depicts the relative absorbance of the 280 nm (circles), 350 nm (squares) and 420 nm (triangles) points in the hardwood UV-Vis absorbance spectra of the second, final alkaline peroxide stage liquors versus the 10 stage peracetate concentration. The dashed lines are provided to help guide the eye.
[0049] FIG. 7 depicts the relative absorbance of the 280 nm (circles), 350 nm (squares) and 420 nm (triangles) points in the softwood UV-Vis absorbance spectra of the D
stage liquors versus the 10 stage peracetate concentration.
[0050] FIG. 8 depicts the relative absorbance of the 280 nm (circles), 350 nm (squares) and 420 nm (triangles) points in the softwood UV-Vis absorbance spectra of the second, final alkaline peroxide stage liquors versus the 10 stage peracetate concentration.
[0051] While the invention is susceptible to various modifications and alternative forms, specific embodiments thereof are shown by way of example in the drawings and may herein be described in detail. The drawings may not be to scale. It should be understood, however, that the drawings and detailed description thereto are not intended to limit the invention to the form disclosed, but on the contrary, the intention is to cover all modifications, equivalents and alternatives falling within the spirit and scope of the present invention as defined by the appended claims.
* * *
[0052] The headings used herein are for organizational purposes only and are not meant to be used to limit the scope of the description. As used throughout this application, the word "may" is used in a permissive sense (i.e., meaning having the potential to), rather than the mandatory sense (i.e., meaning must). The words "include," "including," and "includes"
indicate open-ended relationships and therefore mean including, but not limited to. Similarly, the words "have,"
"having," and "has" also indicated open-ended relationships, and thus mean having, but not limited to. The terms "first," "second," "third," and so forth as used herein are used as labels for nouns that they precede, and do not imply any type of ordering (e.g., spatial, temporal, logical, etc.) unless such an ordering is otherwise explicitly indicated. Similarly, a "second"
feature does not require that a "first" feature be implemented prior to the "second" feature, unless otherwise specified.
[0053] Various components may be described as "configured to" perform a task or tasks. In such contexts, "configured to" is a broad recitation generally meaning "having structure that"
performs the task or tasks during operation. As such, the component can be configured to perform the task even when the component is not currently performing that task. In some contexts, "configured to" may be a broad recitation of structure generally meaning "having a feature that"
performs the task or tasks during operation. As such, the component can be configured to perform the task even when the component is not currently on.
[0054] Various components may be described as performing a task or tasks, for convenience in the description. Such descriptions should be interpreted as including the phrase "configured to." Reciting a component that is configured to perform one or more tasks is expressly intended not to invoke 35 U.S.C. 112 paragraph (f), interpretation for that component.
[0055] The scope of the present disclosure includes any feature or combination of features disclosed herein (either explicitly or implicitly), or any generalization thereof, whether or not it mitigates any or all of the problems addressed herein. Accordingly, new claims may be formulated during prosecution of this application (or an application claiming priority thereto) to any such combination of features. Regarding the appended claims, features from dependent claims may be combined with those of the independent claims and features from respective independent claims may be combined in any appropriate manner and not merely in the specific combinations enumerated in the appended claims.
[0056] It is to be understood the present invention is not limited to particular devices or biological systems, which may, of course, vary. It is also to be understood that the terminology used herein is for describing embodiments only, and is not intended to be limiting. As used in this specification and the appended claims, the singular forms "a", "an", and "the"
include singular and plural referents unless the content clearly dictates otherwise. Thus, for example, reference to "a linker" includes one or more linkers.
DETAILED DESCRIPTION
DEFINITIONS
[0057] Unless defined otherwise, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art.
[0058] The term "about" as used herein generally refers to a descriptor that modifies a quantifiable amount (unless otherwise defined herein or as a generally accepted term of art) by plus or minus ten percent.
[0059] The term "reactive oxygen species" as used herein generally refers to a species such as may include singlet oxygen (102), superoxide radical (021, hydroperoxyl radical (H00.), hydroxyl radical (HO.), acyloxy radical (RC(0)-0.), and other activated or modified forms of ozone (e.g., ozonides and hydrogen trioxide). Each of these ROS has its own oxidation potential, reactivity/compatibility profile, compatibility/selectivity and half-life.
[0060] The term "reactive species oxidant" as used herein generally refers to oxidant formulations containing or capable of evolving at least one reactive oxygen species and can evolve at least one reactive carbon species. Such reactive species enhance the oxidative or reductive performance of the precursor formulation constituents.
[0061] The term "pulp" as used herein generally refers to a suspension of cellulose fibers in water consisting of any lignocellulose-containing material derived from natural sources such as, but not limited to, hardwood, softwood, bamboo, eucalyptus, wheat straw, rice and other plant-based sources, straw, bagasse and/or bamboo and such pulp produced by various chemical, semichemical, thermal or mechanical pulping processes or a combination pulping processes.
[0062] The terms "delignifying" and "delignification" as used herein generally refers to removal of lignin from wood and non-wood fibers by mechanical, chemical or enzymatic means or a combination thereof the polymer lignin from wood.
[0063] The term "bleaching" as used herein generally refers to a chemical process used to whiten and purify pulp and the processing of wood to decrease the color of the pulp and to make it whiter.
[0064] The term "brightening" as used herein generally refers to increasing the reflectance and/or whiteness of fibers, which may be related to a reduction in kappa number and/or the oxidation and removal of colored materials or color-forming materials from pulp.
[0065] The term "pulp treatment process" as used herein generally refers at least one of pulping, delignification and bleaching.
[0066] The term "liquor" as used herein generally refers to black liquor, oxidant liquor, bleaching liquor, pulping liquor and wash liquor drained from the pulp during and/or after pulping, delignification and bleaching processes.

EMBODIMENTS
[0067] In some embodiments, the ROS formulation described herein, which generates singlet oxygen in significant quantities, has significant beneficial impacts on delignification, lignin extraction and bleaching of pulp. A singlet oxygen stage used at the beginning of a bleach sequence or used within a bleach sequence, when followed by an alkaline peroxide stage, significantly reduces the amount of chlorine dioxide (C102) needed to achieve brighter and white grades of pulp. Singlet oxygen delignification may be used to increase the efficiency of lignin extraction and brightening at subsequent bleaching stages, including stages that are two, three or more steps after a singlet oxygen stage. The increased lignin extraction and brightening efficiency enabled by using the ROS formulation in a ECF bleach sequence enables the use of up to about 97% less C102 to produce pulp brightness of about 60% ISO or greater.
Elimination of C102 from a bleach sequence may be enabled by employing more than one pair of singlet oxygen and alkaline peroxide stages in a bleaching sequence.
[0068] The use of singlet oxygen in a bleach sequence has several important impacts on pulp production performance, economics, operations and pollution prevention. In some embodiments, it may eliminate up to 97% C102 use in an elemental chlorine free (ECF) bleach sequence to achieve pulp brightness of about 60% ISO or greater. It may eliminate the need for C102 use by enabling more effective totally chlorine free (TCF) bleach sequences. It may increase pulp yield in proportion to maintaining higher kappa number of pulp during a bleach sequence. It may increase bleached fiber strength in proportion to maintaining higher viscosity of pulp fiber during a bleach sequence. It may produce brighter fiber grades without a conventional bleach plant. It may reduce absorbable organic halide (AOX) effluent in proportion to the reduction of C102 use.
It may reduce the amount of wastewater generated in a bleach plant for treatment and disposal. It may reduce corrosion in a bleach plant in proportion to the reduction of C102 use. It may increase safety in a bleach plant by significantly reducing the amount of C102 used in a process. It may reduce the amount of water used in a bleach plant. It may increase water recycling in a pulp mill with a bleach plant by conducting singlet oxygen and peroxide stages in the pulp plant.
[0069] The peracetate formulation comprising the reactive oxygen species (ROS) formulation described herein may generate singlet oxygen as its primary ROS. Singlet oxygen is particularly efficient at oxidizing aromatic rings and unsaturated hydrocarbons (alkenes or olefins), which dominate the structure of lignin or are produced during chemical pulping processes. Singlet oxygen oxidation may be selective towards unsaturated hydrocarbons and phenolic materials comprising lignin and, as a result, has low impact on cellulose fibers compared to less selective oxidants that may generate significant quantities of free radicals or are free radicals in their native form including alkaline hydrogen peroxide, ozone, chlorine dioxide, elemental chlorine, free chlorine and hydroxyl radicals.
[0070]
Singlet oxygen provided by the ROS formulation described herein was found to impact lignin structures in a manner that provides rapid and extensive delignification and extraction of lignin from a variety of pulps including sulfate pulps and oxygen-delignified pulps having medium kappa numbers (e.g., 10-50 kappa number), but also degrades lignin structures in away that allows for traditional chemical bleaching treatments to more efficiently and extensively extract and remove lignin and other colored materials from pulp prior to, during and after bleaching with C102.
[0071]
Delignification and brightening driven by the ROS formulation enables a significant reduction in the use of C102 bleaching in a conventional ECF bleaching process to achieve brighter grades of pulp. Pulp brightness of about 60% ISO or greater can be achieved with up to about a 97% reduction of C102 use relative to many conventional ECF bleach sequences.
Pulp brightness of about 80% ISO or greater can be achieved with up to about a 95% reduction of C102 use relative to many conventional ECF bleach sequences. Alternatively, C102 may be eliminated from a bleach sequence to conduct TCF bleaching. The key to this ability is enabling the selective oxidation, damage and extraction of lignin, non-lignin colored materials and color-forming materials (e.g., hexenuronic acids, HexA) with singlet oxygen. These materials are generally composed of phenol structures, olefin structures, aromatic and non-aromatic hydrocarbons. Singlet oxygen can undergo [2+2] and [4+2] Diels-Alder type cycloadditions with olefins, phenols and other aromatic hydrocarbons efficiently. Singlet oxygen can also undergo "ene reactions" with alkenes or olefins.
These singlet oxygen reaction mechanisms are relatively selective toward olefins, phenols and other aromatic hydrocarbons. Elevated temperature accelerates reaction rates considerably for these reactions leading to rapid delignification and oxidative degradation of phenolic materials while having little impact on cellulose fiber.
[0072] Free radical species (e.g., superoxide, hydroperoxyl, hydroxyl and alkoxyl radicals) are known to cause depolymerization of polysaccharides.
Oxidative depolymerization of polysaccharides is known to be initiated by hydrogen abstraction by a free radical species leading to 13-scission reactions and breakdown of polysaccharide chains. Highly alkaline conditions (e.g., pH 11 and greater) can also cause polysaccharide breakdown through base hydrolysis or alkaline hydrolysis of glycosidic bonds. Depolymerization causes a decrease in viscosity of polysaccharide solutions. Viscosity is the basis for one standard method of measuring the impact of chemical treatments on pulp fiber, which is composed of cellulosic structures made of polysaccharides.
[0073]
Kappa number is generally a measure of the amount of materials in pulp that can be oxidized by permanganate and is proportional to lignin content, but can include non-lignin materials formed from hemicellulose materials during chemical pulping and oxygen delignification processes. Pulp bleaching removes residual lignin, but the use of strong bleaching chemicals such as chlorine, chlorine dioxide and ozone may also remove residual hemicellulose and cause non-selective oxidative degradation and loss of the cellulose fibers. Removal of lignin, .. hemicellulose and cellulose from pulp results in reduction of pulp yield relative to the initial mass of wood entering a pulp mill or bleach plant. Removal of less material from the pulp, as indicated by significantly higher kappa numbers associated with a given brightness, can increase pulp yield.
[0074] In an elemental chlorine free (ECF) bleaching sequence C102 is commonly used to do a significant delignification step in a first bleaching stage, often designated as Do. This delignification allows high brightness to be achieved more efficiently in subsequent bleaching stages, which are often designated as Di and Dz. An alkaline extraction stage is often used after Do and the bleach sequence may be finished with a hydrogen peroxide stage to provide additional brightening and reduce color reversion. This is a common ECF bleaching approach to produce bleached "market pulp" with a brightness of 85% ISO and a kappa number of about 1. The total amount of C102 used in this sequence may range between about 45 to 90 lbs C102 per oven dry ton of pulp depending on several factors including the pulp species, pulping and delignification methods used, kappa number prior to bleaching and bleaching process conditions.
[0075] The majority of C102 (e.g., 60-90%) is used in a Do stage, which is also when the majority of absorbable organic halide (AOX) and AOX waste stream is produced.
Some examples of toxic AOX byproducts from pulp bleaching include chlorophenols, chlorobenzenes, chlorofurans, chloroform and dioxins. Eliminating the Do stage by using singlet oxygen and hydrogen peroxide stages will eliminate the majority AOX waste stream.
[0076] Chlorine dioxide, its chlorinated precursors and byproducts (e.g., chlorite, chlorate) and chloride salt byproducts are not compatible with recovery boilers and other equipment in pulp plants where water and liquor materials are reused in closed-loop cycles. As a result, the use of chlorine and C102 is limited to bleach plants where the bleach plant water effluent is a toxic waste stream.
[0077] In some embodiments, the use of a singlet oxygen stage followed by an alkaline hydrogen peroxide stage at least once in a bleaching sequence provides the ability to brighten fiber significantly without a conventional bleach plant. The use of the ROS
formulation to deliver singlet oxygen in large quantities as a liquid ROS formulation into a pulping process creates an opportunity to add chemical brightening steps to an existing fiber line without the large capital costs needed to build conventional bleaching facilities.
[0078] In some embodiments, the ROS-generating peracetate formulation described herein may be used for delignification and extraction of materials from pulp fibers for brightening and bleaching purposes. It may also be used for extracting lignin from cellulosic fibers for the recovery of lignin from the black liquor or spent oxidant liquor.
[0079] It was discovered that the full potential of a singlet oxygen treatment of pulp is realized in subsequent treatment steps or bleaching stages. In some embodiments, singlet oxygen is effective at breaking down and extracting lignin and other materials from pulp in a selective manner that can have little to no derogatory impact on cellulose fibers. In some embodiments, singlet oxygen may damage lignin and other colored or color-forming materials in pulp in a way that allows an alkaline hydrogen peroxide treatment step to extract lignin and other colored or color-forming materials from pulp more efficiently than without the use of singlet oxygen.
[0080] In some embodiments, one preferred ROS-producing oxidant formulation is a peracetate solution. The peracetate solution may include generating an alkaline hydrogen peroxide solution from the combination of an alkali and a hydrogen peroxide concentrate, mixing the alkaline hydrogen peroxide solution with an acyl donor such that a peracetate solution concentrate is formed. In some embodiments, the peracetate solution may include peracetate anions and a peracid. In some embodiments, the peracetate solution may include a pH from about pH 10 to about pH 12. In some embodiments, the peracetate solution has a molar ratio of peracetate anions to peracid ranging from about 60:1 to about 6000:1. ROS-generating peracetate oxidant solutions may contain no hydrogen peroxide, and are produced on site and on demand at alkaline pH. The peracetate oxidant solution produces multiple ROS by itself and when placed into contaminated environments. In some embodiments, the ROS most important in peracetate oxidant solutions include singlet oxygen, superoxide radical, hydroperoxyl radical, acetyloxy radical and potentially other radical fragments. When a combination of these ROS are generated together in peracetate oxidant solutions they produce an oxidative-reductive potential (ORP) response in water that may exceed 900 mV (vs standard hydrogen electrode) around pH 7. These solutions may be more convenient and effective to use than other approaches. The dominant ROS may be selectively reactive such that they are effective in a variety of environments.
[0081] In some embodiments, a method may include making a reactive species formulation.
The method may include providing an alkaline hydrogen peroxide solution. The method may include contacting the alkaline hydrogen peroxide solution with an acyl donor.
A peracid concentrate may be produced by the contacting of the alkaline hydrogen peroxide with the acyl donor. The peracid concentrate may have a molar ratio of hydrogen peroxide to acyl donor reactive groups ranging from about 1:1.25 to about 1:4. The method may include maintaining the peracid concentrate pH value in a range from about pH 10 to about pH 12. Singlet oxygen sources and methods of their production are further described at in U.S. Patent No.
9,517,955 to Buschmann and U.S. Patent Application No. 15/371,872 to Buschmann, both of which are incorporated in their entirety herein.
[0082] In some embodiments, thermal acceleration of the reaction(s) that produce ROS, especially singlet oxygen, from the "parent" peracetate formulation is particularly important to performance. In some embodiments increasing the temperature of the peracetate oxidant in pulp treatment accelerates bleaching rate by increasing the production rate and concentration of ROS.
In some embodiments, heating or thermal acceleration or activation of peracetate oxidant solutions to a temperature between about 50 C to about 95 C accelerates the formation of ROS (singlet oxygen) from a "parent" peracetate formulation to increase rates of bleaching with increasing temperature.
[0083] It was unexpectedly discovered that extraction of lignin from pulp with singlet oxygen increased the amount of lignin and other colored materials that could be extracted in subsequent stages by alkaline hydrogen peroxide and chlorine dioxide such that much less C102 may be used to achieve high brightness levels. It was discovered that the amount of lignin and other materials extracted into the liquors of chlorine dioxide and alkaline hydrogen peroxide stages, which were two or more stages after singlet oxygen treatment, increased in proportion to the amount of singlet oxygen used. This discovery was made by examining the extracted materials in the liquors recovered from each bleach stage using ultraviolet and visible (UV-Vis) absorption spectroscopy.
[0084] FIG. 1 shows examples of UV-Vis absorption spectra of alkaline hydrogen peroxide liquors drained from north American hardwood and softwood (pine) sulfide pulps after conventional oxygen delignification. Liquors from singlet oxygen and chlorine dioxide stages have similar characteristic absorption spectra features. The absorption band centered around 280 nm is a characteristic of lignin. The absorption band centered around 350 nm is associated with the ionized, anion forms of phenols and hydroquinones in the extracted lignin.
This absorbance band extends into the visible part of the spectrum (greater than about 380 nm) and imparts yellow color to pulp. The very broad absorption that extends above 420 nm tends to impart more orange to red hues to pulp. Removing materials from pulp that contribute to the 350 and 420 nm absorption band intensities is important to producing brighter and whiter pulp fiber. The more materials extracted into the liquors the greater the intensity of the absorption bands. It was generally found that the intensities of these characteristic absorption bands, and corresponding amounts of extracted materials, from the final C102 and alkaline peroxide stages increased with
85 increasing amount of singlet oxygen used earlier in the bleach sequence. These trends were observed for hardwood and softwood pulps as described in the examples.
[0085] In an embodiment, measuring and analyzing the UV-Vis absorption spectra of liquors from a bleaching sequence provides a method of monitoring pulp bleaching performance, a method .. of controlling the amount of chemistry used in a specific bleaching stage to control the brightness achieved in a specific bleaching stage or in a subsequent stage or stages.
[0086] The UV-Vis absorption spectra of liquors after each stage in a pulp bleaching sequence may be correlated with the amount of chemistry used in a specific bleaching step to achieve a specified brightness of pulp. For example, it was found that characteristic absorption band intensities of liquors from the D and P2 stages increased with increasing singlet oxygen treatment (increasing peracetate concentration) to achieve an increasing level of pulp brightness in the 10 Pi D P2 bleach sequence. Characteristic absorption band intensities of liquors from the D stage could be increased by increasing the amount of chlorine dioxide used to achieve an increasing level of pulp brightness. Characteristic absorption band intensities of liquors from the 10 and Pi stage were dependent on the amount of singlet oxygen treatment (peracetate concentration) and/or hydrogen peroxide concentration, and/or pH of the hydrogen peroxide treatment.
Depending on the process conditions, the absorption band intensities increased or decreased in response to changing one or more of these parameters.
[0087] The UV-Vis absorption spectra of liquors may be measured continuously during a pulp bleaching process using a spectrometer outfitted with a flow-through sample chamber for slip-stream analysis of liquors separated from the bleaching process. The UV-Vis absorption spectra of liquors may be measured continuously during a pulp bleaching process using a spectrometer outfitted with a multi-fiber optical cable apparatus or other suitable optical apparatus that may be inserted into a process stream. Such apparatuses would allow for real-time bleaching process monitoring and control feedback data to be generated and used to control chemical use in a bleaching process and to provide a method of quality control in a bleaching process.
[0088] It was unexpectedly discovered that delignification and brightening with singlet oxygen could cause an increase in the measured viscosity of pulp fiber. This discovery indicates that the singlet oxygen ROS formulation may not have a significant negative impact on the pulp fiber's cellulosic structure. Under natural pH or pulp pH conditions in a mill fiber line (e.g., pH 6.0-10.8) the singlet oxygen ROS formulation can have little to no impact on pulp viscosity in a bleach sequence.
[0089] FIG. 2 depicts the brightness of pulp after each bleach stage for a north American hardwood pulp, after sulfide pulping and conventional oxygen delignification stages, 0, bleached with the following sequence: 10 PD P where 10 is singlet oxygen, P is alkaline hydrogen peroxide and D is chlorine dioxide. Pulp consistency was 5% during each bleach stage at 75 C. The singlet oxygen stage was provided by a 800 mg/kg charge of peracetate (added as a 2%
sodium peracetate solution formulation) to the pulp. The initial oxygen delignified pulp had a brightness of 49.10%
.. ISO. After the singlet oxygen stage the brightness was 55.87% ISO. The alkaline hydrogen peroxide stage increased brightness to 64.90% ISO. The C102 stage increased brightness to 71.38% ISO. The final alkaline peroxide stage increased brightness to 78.88%
ISO. This sequence used only 4 lb C102 per oven dry ton of pulp as compared to between about 45 to 90 lbs C102 per oven dry ton of pulp commonly used in ECF bleaching sequences to produce market pulp with a brightness of 85% ISO.
[0090] Consistent with the UV-Vis absorption spectra trends for the D
and P liquors, when the peracetate charge for the singlet oxygen stage increased from 600 to 800 to 1000 mg/kg pulp and all other stages were kept the same the corresponding final brightness values increased from 76.78 to 78.88 to 79.57% ISO, respectively.
[0091] FIG. 3 depicts viscosity of the above north American hardwood pulp treated with 800 mg/kg peracetate (added as a 2% sodium peracetate solution formulation) in the singlet oxygen stage. The bleach sequence was 10 P D P. The initial oxygen delignified pulp had a viscosity of 19.42 centipoise (cP). After the singlet oxygen stage the viscosity increased slightly to 20.76 cP.
The alkaline hydrogen peroxide stage decreased the viscosity to 15.02 cP. The C102 stage decreased the viscosity only slightly to 14.92 cP. The final alkaline peroxide stage decreased viscosity to 11.87. The increase in viscosity after the singlet oxygen stage is unusual and unexpected relative to the impact it had on the rest of the bleaching sequence. The dramatic reduction in C102 use in this sequence minimized its impact on viscosity. The alkaline peroxide stages were the most damaging to the pulp fiber with the largest viscosity decreases. The conditions for the P stages may be optimized to reduce the degradative impact of the P stages on viscosity by using standard practices including optimizing the amount of hydrogen peroxide and alkali used, adding a chelation wash before the first P stage or adding magnesium sulfate with the P stage.
[0092] In the methods described herein an unexpected discovery was that using singlet oxygen in a bleaching sequence increased pulp brightness with significantly less corresponding reduction in kappa number than conventionally bleached pulps (e.g., ECF bleach sequences). Pulp yield has been correlated with kappa number in the pulp industry and this correlation is generally consistent for each wood species. For example, hardwood species like spruce and birch bleached to a brightness of 85% ISO typically have a kappa number of about 1. The result of higher kappa numbers being obtained at higher brightness values indicates that the pulp yield for bleached grades can be increased by using at least one singlet oxygen stage in a bleaching sequence.
[0093] FIG. 4 shows ISO brightness vs kappa number for the above north American hardwood pulp, treated with 800 mg/kg peracetate (added as a 2% sodium peracetate solution formulation) in the singlet oxygen stage. The solid circles show the relationship between ISO brightness and kappa number for pulp bleaching sequences incorporating 10 P and 10 Q P
relative to market pulp (open square) bleached with a conventional ECF bleach sequence. The initial pulp before bleaching had a 49.10% ISO brightness with a kappa number of 15.05. After the 10 stage the pulp had a 55.87% ISO brightness with a kappa number of 9.60. After a 10 P sequence the pulp had a 64.90% ISO brightness with a kappa number of 7.46. After a 10 P D P sequence the pulp had a 78.88% ISO brightness with a kappa number of 5.31. After a 10 QPDP sequence the pulp had a 85.10% ISO brightness with a kappa number of 4.42. Hardwood market pulp was analyzed as a standard control sample and had a 85.76% ISO brightness with a kappa number of 1.11.
[0094] A brightness of 85.10% ISO was achieved at a kappa number of 4.42, which was four times greater than the kappa number of standard hardwood market pulp with 85.76% ISO
brightness. These results demonstrate that the use of singlet oxygen and alkaline hydrogen peroxide enables the oxidation and removal of colored materials from pulp without removing as much material from the pulp as conventional ECF bleaching (e.g., oxygen delignification followed by DEDD bleach sequence) used to produce market pulp. The higher kappa number at a given brightness when using singlet oxygen and alkaline hydrogen peroxide corresponds to removing less mass of pulp during bleaching, which may provide a greater pulp yield than conventional ECF
bleaching.
[0095] In some embodiments, singlet oxygen may very rapidly oxidize and extract a portion of lignin and non-lignin colored materials from pulp while making residual materials that remain in the pulp fiber more readily extractable in subsequent bleaching stages.
Residual materials may be bound or unbound to pulp fiber structures including hemicellulose structures and cellulose structures. Subsequent bleaching stages may include alkaline hydrogen peroxide, chlorine dioxide, ozone and peracetic acid. In one embodiment, a singlet oxygen stage, 10, is followed by an alkaline hydrogen peroxide stage, P, to significantly increase brightness and reduce the amount of C102 required in an ECF bleaching sequence. A chelating wash stage, Q, may be used just prior to an alkaline hydrogen peroxide stage, but after the 10 stage. A chelating agent used in Q stage may include ethylenediaminetetraacetic acid (EDTA) and diethylenetriaminepentaacetic acid (DTPA). An alkaline hydrogen peroxide stage may include the use of a magnesium salt such as magnesium sulfate. An alkaline hydrogen peroxide stage may be followed by a singlet oxygen stage. A chlorine dioxide stage, D, may be conducted after an alkaline hydrogen peroxide stage.
A chlorine dioxide stage may be followed by subsequent chlorine dioxide, peracetic acid, Paa, alkaline extraction, E, and/or alkaline hydrogen peroxide stages. An ozone stage, Z, may be used before or after any such stages listed above.
[0096] In one embodiment, a preferred bleaching sequence may include 10 P
which may be followed by additional bleaching stages. In some embodiments, the bleaching sequence may be chosen from the following examples: (these examples are not meant to be limiting) lop Q P

lOPZE

10 P Paa P D P
10PDPaaP
lOPZEDP

ZE1OPDP.
[0097] In a preferred embodiment, a bleaching sequence may be singlet oxygen, followed by chelation, followed by alkaline hydrogen peroxide, where the bleaching sequence is represented as 10 Q P. This bleaching sequence may achieve pulp brightness of 60% ISO or greater without further bleaching steps.
[0098] In a preferred embodiment, a bleaching sequence may be singlet oxygen, followed by chelation, followed by alkaline hydrogen peroxide, followed by chlorine dioxide, followed by alkaline hydrogen peroxide, where the bleaching sequence is represented as 10 Q P D P. This bleaching sequence may achieve pulp brightness of 80% ISO or greater without further bleaching steps.
[0099] The impact of singlet oxygen in the bleach sequence 10 P D P was demonstrated on a north American hardwood pulp. The initial oxygen delignified pulp had a kappa number of 15.05 and brightness of 49.10% ISO. The peracetate charge for the singlet oxygen stage was 800 mg/kg pulp. After the singlet oxygen stage the kappa number was 9.60 and brightness was 55.87% ISO.
After the first alkaline peroxide stage the kappa number was 7.46 at and brightness was 64.90%

ISO. After using chlorine dioxide (4.0 lbs per oven dry ton pulp) and a second alkaline peroxide stage the kappa number was 5.31 and brightness was 78.88% ISO.
[00100] When the peracetate charge for the singlet oxygen stage was increased to 1000 mg/kg pulp and all other stages were kept the same the final kappa number was 6.88 and brightness was 79.57% ISO. When the peracetate charge for the singlet oxygen stage was decreased to 600 mg/kg pulp and all other stages were kept the same the final kappa number was 6.12 and brightness was 76.78% ISO. The kappa numbers for the three trials described is significantly greater than the market pulp suggesting that using a singlet oxygen stage and very little chlorine dioxide can extract less material from the pulp, yet still achieve high brightness levels.
Increasing the amount of singlet oxygen used in the bleaching sequence was repeatedly found to increase the final kappa number of the pulp after the entire bleaching sequence when all other variables were held constant.
In some embodiments, the singlet oxygen chemistry provided by the ROS
formulation modifies the pulp in a manner that serves to protect non-colored materials in the pulp from oxidation and extraction in subsequent bleaching stages.
[00101] A bleach sequence consisting of 10 QPDP was used to demonstrate the impact of an EDTA chelating wash stage on pulp quality for a north American hardwood pulp, treated with 800 mg/kg peracetate (added as a 2% sodium peracetate solution formulation) in the singlet oxygen stage. After the 10, Q and P stages the kappa number was 5.67, brightness was 71.80% ISO and viscosity was 20.43 cP. After using chlorine dioxide (8.0 lbs per oven dry ton pulp) and a second alkaline peroxide stage the kappa number was 4.42, brightness was 85.01% ISO
and viscosity was 15.07 cP. Viscosity was preserved through the first alkaline peroxide stage by the chelating wash stage at a value greater than the initial pulp (14.47 cP). The final bleached pulp viscosity was only 4.35 cP lower than the initial unbleached pulp viscosity. An additional benefit of adding the Q
stage was increasing brightness of the pulp by about 6.9% ISO after the 10, Q
and P stages compared to just using 10 and P stages.
[00102] In another embodiment, a bleaching sequence may be singlet oxygen, followed by chelation, followed by alkaline hydrogen peroxide, followed by singlet oxygen, followed by alkaline hydrogen peroxide, where the bleaching sequence is represented as 10 Q P 10 P. This bleaching sequence may achieve pulp brightness of 60% ISO or greater, 70% ISO
or greater, or 80% ISO or greater without further bleaching steps.
EXAMPLES
[00103] Having now described the invention, the same will be more readily understood through reference to the following example(s), which are provided by way of illustration, and are not intended to be limiting of the present invention.
[00104] Test methods: Kappa numbers were measured in duplicate or triplicate using a micro-Kappa procedure that used 0.5 g of oven dried pulp fiber mass (1/4-scale of the standard TAPPI T
236 om-99 method). Kappa number measurements were conducted on pulp samples stored damp after determining the percent solids of each sample.
[00105] The pH of pulp mixtures was measured with a high sodium pH electrode put directly into the pulp slurry. A thermocouple for temperature compensation of the pH
reading was placed in the pulp during measurement.
[00106] Viscosity was measured by the following procedure. Pulp sample was disintegrated and diluted. The slurry was filtered through a filter paper in a Buchner funnel.
The resulting pulp pad was dried at room temperature and solids content was determined. Viscosity of the pulp sample was measured by following Tappi standard T230 with closed bottle procedure.
The reported value is an average of two measurements.
[00107] Brightness measurements were conducted by the following procedure.
Pulp sample was disintegrated in a standard disintegrator at 3000 rpm for 30 seconds. The slurry was diluted and hand sheet was prepared by following Tappi standard procedure T205. Brightness of the air-dry hand sheet was measured in a brightness meter (TECHNIBRITE MODEL MICRO TB-1C).
Eight measurements were taken for each hand sheet sample: four measurements from each side. The reported value is the average of eight measurements.
[00108] The relative amounts of lignin and other materials extracted in each stage of a bleaching sequence were monitored and quantified by measuring the ultraviolet and visible (UV-Vis) absorption spectra of liquors drained from individual pulp bleaching stages.
An example is shown in FIG. 1. Several characteristic absorption bands in the UV-Vis spectra of the liquors were evaluated for their intensity, which were compared between bleaching sequences using systematically varied amounts of chemistry in each stage. The UV-Vis analysis of liquors made it possible to rapidly monitor the impact of a chemical treatment stage on lignin extraction. Several pulp samples throughout the bleaching sequences were analyzed by kappa number, viscosity and brightness measurements.
[00109] To directly compare absorption spectra intensity pulp samples were chemically treated at 5% consistency and 75 C in each bleaching stage. Liquors drained off the pulp were collected for analysis before the pulp was washed with tap water. UV-Vis spectra were measured using an appropriate dilution of the liquor samples with distilled water and pH
adjustment to about pH 10.8-11.4 with 4 molar NaOH. The alkaline sample pH adjustment put the phenolic lignin and oxidized byproducts in their more water soluble and stronger absorbing, ionized forms.
The intensity of characteristic absorption bands centered around 280, 350 and 420 nm were compared on an absolute scale (measured absorbance multiplied by a liquor sample's dilution factor).
[00110] Hardwood Bleaching example 1: A North American hardwood sulfate pulp after oxygen delignification was used to demonstrate the impact of a singlet oxygen stage on the bleaching sequence: 10 Pi D P2, where the subscripts distinguish between different steps with the same abbreviation but not necessarily the same process parameters. The pulp had a consistency of 15.3%, an initial kappa number of 15.05, initial brightness of 49.10% ISO and initial viscosity of 19.42 cP. Each treatment stage of the bleaching sequence was conducted at 5%
consistency (consistency adjusted with distilled water plus chemical charge) with samples hand mixed for 2-3 .. minutes and held at 75 C in a heated water bath. Pulp samples were pre-heated in a microwave oven in 1L glass beakers prior to adding treatment chemicals. After a stage's treatment time the pulp was drained in a Buchner funnel over medium filter paper and a portion of the liquor collected for UV-Vis analysis. Then the pulp was washed with a fixed amount of warm tap water (e.g., 200 g of the original 15.3% consistency pulp was washed with 1200 mL water). The thickened pulp was then recovered and treated in the next stage of the sequence. Pulp samples of each stage were prepared and stored damp and refrigerated (about 3-6 C) prior to fiber analyses for kappa number, brightness and viscosity.
[00111] Each of the three trial sequences was conducted using the same parameters except for the amount of singlet oxygen used, which was determined by the charge of sodium peracetate formulation in the pulp. The singlet oxygen stage, 10, was conducted by rapidly mixing into the pre-heated pulp with the appropriate volume of 2.0% peracetate solution (excluding the molecular weight of sodium) to make initial concentrations of 600, 800 and 1000 mg/kg in the 5%
consistency pulp (trial sequences 1, 2 and 3, respectively). The 10 stage was held at temperature for 5 minutes in all trials. In subsequent stages the same chemical charge was used for each trial sequence. Stage Pi used 900 mg/kg hydrogen peroxide and 1700 mg/kg sodium hydroxide in 5%
consistency pulp (post-mixing pulp pH was about 11.3). Stage Pi was held at temperature for 30 minutes. Stage D used 100 mg/kg chlorine dioxide (post-mixing pulp pH was about 4.4) and was held at temperature for 5 minutes. Stage P2 used 600 mg/kg hydrogen peroxide and 1460 mg/kg sodium hydroxide in 5% consistency pulp (post-mixing pulp pH was about 11.4).
Stage P2 was held at temperature for 30 minutes.
[00112] UV results: The absorbance intensity at 280, 350 and 420 nm in the UV-Vis absorbance spectra of the liquors recovered from the D and P2 stages in the three bleaching sequence trials increased with increasing initial concentration of peracetate in the singlet oxygen stage, 10. FIG.
5 shows the extraction of optically absorbing materials by chlorine dioxide, D, increases with increasing amount of singlet oxygen. FIG. 6 shows the extraction of optically absorbing materials by alkaline hydrogen peroxide, P2, after the chlorine dioxide stage, increases with increasing amount of singlet oxygen.
[00113] Fiber results: For trial sequence 1 (600 mg/kg initial peracetate) the final post-P2 fiber analyses were kappa number 6.12, brightness 76.78% ISO and viscosity 12.85 cP.
For trial sequence 2 (800 mg/kg initial peracetate) the final post-P2 fiber analyses were kappa number 5.31, brightness 78.88% ISO and viscosity 11.87 cP. For trial sequence 3 (1000 mg/kg initial peracetate) the final post-P2 fiber analyses were kappa number 6.88, brightness 79.57% ISO
and viscosity 11.66 cP.
[00114] For trial sequence 2 (800 mg/kg initial peracetate) fiber analyses were also conducted after each stage in the sequence. After 10 the fiber analyses were kappa number 9.60, brightness 55.87% ISO and viscosity 20.76 cP. After Pi the fiber analyses were kappa number 7.46, brightness 64.90% ISO and viscosity 15.02 cP. After D the fiber analyses were brightness 71.38%
ISO and viscosity 14.92 cP. After P2 the fiber analyses were kappa number 5.31, brightness 78.88% ISO and viscosity 11.87 cP.
[00115] Hardwood Bleaching example 2: A north American hardwood sulfate pulp after oxygen delignification was used to demonstrate the impact of a singlet oxygen stage on the bleaching sequence: 10 Q Pi D P2, where the subscripts distinguish between different steps with the same abbreviation but not necessarily the same process parameters. The pulp had a consistency of 15.3% an initial kappa number of 15.05, initial brightness of 49.10% ISO
and initial viscosity of 19.42 cP. Each treatment stage of the bleaching sequence was conducted at 5% consistency (consistency adjusted with distilled water plus chemical charge) with samples hand mixed for 2-3 minutes and held at 75 C in a heated water bath. Pulp samples were pre-heated in a microwave oven in 1L glass beakers prior to adding treatment chemicals. After a stage's treatment time the pulp was drained in a Buchner funnel over medium filter paper and a portion of the liquor collected for UV-Vis analysis. Then the pulp was washed with a fixed amount of warm tap water (e.g., 200 g of the original 15.3% consistency pulp was washed with 1200 mL water). The thickened pulp was then recovered and treated in the next stage of the sequence. Pulp samples of each stage were prepared and stored damp and refrigerated (about 3-6 C) prior to fiber analyses for kappa number, brightness and viscosity.
[00116] The singlet oxygen stage, 10, was conducted by rapidly mixing into the pre-heated pulp the appropriate volume of 2.0% peracetate solution (excluding the molecular weight of sodium) to make initial concentrations of 800 mg/kg in the 5% consistency pulp. The 10 stage was held at temperature for 5 minutes. The chelation wash stage, Q, used 0.4 wt% EDTA per oven dry ton of pulp, which was mixed into the pulp and the pulp pH adjusted to pH
5.0 with dilute sulfuric acid. This mixture was held at temperature for 5 min before draining.
Stage Pi used 900 mg/kg hydrogen peroxide and 1700 mg/kg sodium hydroxide in 5% consistency pulp (post-mixing pulp pH was about 11.3). Stage Pi was held at temperature for 30 minutes.
Stage D used 200 mg/kg chlorine dioxide (post-mixing pulp pH was about 3.2) and was held at temperature for 5 minutes. Stage P2 used 600 mg/kg hydrogen peroxide and 1460 mg/kg sodium hydroxide in 5%
consistency pulp (post-mixing pulp pH was about 11.4). Stage P2 was held at temperature for 30 minutes.
[00117] Fiber results: After the 10, Q and P stages the kappa number was 5.67, brightness was 71.80% ISO and viscosity was 20.43 cP. After using chlorine dioxide (8.0 lbs per oven dry ton pulp) and a second alkaline peroxide stage the kappa number was 4.42, brightness was 85.01%
ISO and viscosity was 15.07 cP. Viscosity was preserved through the first alkaline peroxide stage by the chelating wash stage at a value greater than the initial pulp (14.47 cP). The final bleached pulp viscosity was only 4.35 cP less than the initial unbleached pulp viscosity. An additional benefit of adding the Q stage was increasing brightness of the pulp by about 6.9% ISO after the 10, Q and P stages compared to just using 10 and P stages in the preceding example.
[00118] Softwood Bleaching example: A north American softwood (pine) sulfate pulp after oxygen delignification was used to demonstrate the impact of two singlet oxygen stages on the bleaching sequence: 101 P1 102 P2 D P3. The pulp had a consistency of 16.2% an initial kappa number of 38.66. Each treatment stage of the bleaching sequence was conducted at 5%
consistency (consistency adjusted with distilled water plus chemical charge) with samples hand mixed for 2-3 minutes and held at 80 C in a heated water bath. Pulp samples were pre-heated in a microwave oven in 1L glass beakers prior to adding treatment chemicals.
After a stage's treatment time the pulp was drained in a Buchner funnel over medium filter paper and a portion of the liquor collected for UV-Vis analysis. Then the pulp was washed with a fixed amount of warm tap water (e.g., 200 g of the original 16.2% consistency pulp was washed with 1200 mL water).
The thickened pulp was then recovered and treated in the next stage of the sequence. Pulp samples of each stage were prepared and stored damp and refrigerated (about 3-6 C) prior to fiber analyses for kappa number.
[00119] Each of the two trial sequences were conducted using the same parameters except for the amount of singlet oxygen used in the first stage, 101, which was determined by the charge of sodium peracetate formulation in the pulp. The 101 stage was conducted by rapidly mixing into the pre-heated pulp the appropriate volume of 2.0% peracetate solution (excluding the molecular weight of sodium) to make initial concentrations of 800 and 1100 mg/kg in the 5% consistency pulp (trial sequences 1 and 2 respectively). The 10 stage was held at temperature for 5 minutes in all trials. In subsequent stages the same chemical charge was used for each trial sequence. Stage Pi used 900 mg/kg hydrogen peroxide and 1800 mg/kg sodium hydroxide in 5%
consistency pulp (post-mixing pulp pH was about 11.5). Stage Pi was held at temperature for 30 minutes. Stage 102 used 600 mg/kg peracetate and was held at temperature for 5 minutes. Stage P2 used 800 mg/kg hydrogen peroxide and 1500 mg/kg sodium hydroxide in 5% consistency pulp (post-mixing pulp pH was about 11.4). Stage P2 was held at temperature for 30 minutes.
Stage D used 100 mg/kg chlorine dioxide (post-mixing pulp pH was about 4.4) and was held at temperature for 5 minutes. Stage P2 used 600 mg/kg hydrogen peroxide and 1100 mg/kg sodium hydroxide in 5%
consistency pulp (post-mixing pulp pH was about 11.2). Stage P2 was held at temperature for 30 minutes.
[00120] UV results: The absorbance intensity at 280, 350 and 420 nm in the UV-Vis absorbance spectra of the liquors recovered from the D and P3 stages in the three bleaching sequence trials increased with increasing initial concentration of peracetate in the 101 singlet oxygen stage. FIG. 7 shows the extraction of optically absorbing materials by chlorine dioxide, D, increases with increasing amount of singlet oxygen. FIG. 8 shows the extraction of optically absorbing materials by alkaline hydrogen peroxide, P3, after the chlorine dioxide stage, increases with increasing amount of singlet oxygen.
[00121] The UV-Vis absorbance results suggest that the amount of material extracted in the D
and P3 stages is influenced by the combined total amount of singlet oxygen used in the bleach sequence incorporating multiple 10 stages.
[00122] Substituting the 102 stage with a Paa stage was less effective in brightening and resulted in less lignin extraction during the D and P3 stages as measured by the UV-Vis absorbance of liquor extracts. The use of an acidic peracid treatment step may be useful in other bleaching sequences and with other fiber species that can benefit from an oxidative peracid hydrolysis treatment step. A hydrogen peroxide-free peracid solution can be produced by addition of an acid to pulp containing the peracetate formulation when the pH of the pulp is reduced to less than pH
6. An acid may include sulfuric acid, hydrochloric acid, nitric acid, phosphoric acid, sodium bisulfate, sulfamic acid, acetic acid and citric acid.
[00123] Conducting the above sequences at 15% pulp consistency gave the same trends in the UV-Vis absorbance of liquor extracts from the D and P3 stages.
[00124] Fiber results: For trial sequence 1 (800 mg/kg initial peracetate) the post-P3 fiber kappa number was 13.77 and the brightness was estimated to be approximately 55-60% ISO. For trial sequence 2 (1100 mg/kg initial peracetate) the post-P3 fiber kappa number was 11.70 and the brightness was estimated to be approximately 55-60% ISO. The pulp brightness was visibly greater for trial sequence 2.
[00125] In this patent, certain U.S. patents, U.S. patent applications, and other materials (e.g., articles) have been incorporated by reference. The text of such U.S. patents, U.S. patent applications, and other materials is, however, only incorporated by reference to the extent that no conflict exists between such text and the other statements and drawings set forth herein. In the event of such conflict, then any such conflicting text in such incorporated by reference U.S.
patents, U.S. patent applications, and other materials is specifically not incorporated by reference in this patent.
[00126] Further modifications and alternative embodiments of various aspects of the invention will be apparent to those skilled in the art in view of this description.
Accordingly, this description is to be construed as illustrative only and is for the purpose of teaching those skilled in the art the general manner of carrying out the invention. It is to be understood that the forms of the invention shown and described herein are to be taken as the presently preferred embodiments. Elements and materials may be substituted for those illustrated and described herein, parts and processes may be reversed, and certain features of the invention may be utilized independently, all as would be apparent to one skilled in the art after having the benefit of this description of the invention.
Changes may be made in the elements described herein without departing from the spirit and scope of the invention as described in the following claims.

Claims (27)

WHAT IS CLAIMED IS:
1. A method of bleaching pulp, comprising:
contacting a pulp with a singlet oxygen source; and contacting the pulp with an alkaline peroxide source.
2. The method of claim 1, further comprising repeatedly contacting the pulp in multiple stages with a singlet oxygen source and/or an alkaline peroxide source.
3. The method of claim 1, further comprising repeatedly contacting the pulp with a singlet oxygen source and/or an alkaline peroxide source such that the resulting bleached pulp comprises a pulp brightness of about 80% ISO or greater.
4. The method of claim 3, further comprising collecting a liquor and sending the liquor to a recovery boiler or a lignin recovery process.
5. The method of claim 1, wherein the bleached pulp comprises a pulp brightness of about 60%
ISO or greater.
6. The method of claim 5, further comprising contacting the pulp with an alkaline peroxide source such that the resulting bleached pulp comprises a pulp brightness of about 85%
ISO or greater.
7. The method of claim 1, further comprising contacting the pulp with chlorine dioxide.
8. The method of any one of claims 1-7, further comprising:
monitoring at least one of absorbance spectra of bleaching liquors, kappa number, fiber brightness, or fiber viscosity; and optimizing a bleaching sequence based upon the monitored values.
9. The method of claim 1, wherein the singlet oxygen source comprises a peracetate oxidant solution.
10. The method of claim 9, wherein the peracetate oxidant solution comprises peracetate anions and a peracid, wherein the peracetate oxidant solution has a pH from about 7 to about pH 12, and wherein the peracetate oxidant solution has a molar ratio of peracetate anions to peracid ranging from about 60:1 to about 6000:1.
11. The method of claim 1, wherein the contacting the pulp with the singlet oxygen source preserves pulp viscosity.
12. A method of bleaching pulp, comprising:
contacting a pulp with a singlet oxygen source;
contacting the pulp with a chelating agent; and contacting the pulp with an alkaline peroxide source.
13. The method of claim 12, further comprising repeatedly contacting the pulp in multiple stages with a singlet oxygen source and/or an alkaline peroxide source.
14. The method of claim 12, wherein the bleached pulp comprises a pulp brightness of about 60%
ISO or greater.
15. The method of claim 12, further comprising contacting the pulp with chlorine dioxide.
16. The method of claim 15, further comprising contacting the pulp with an alkaline peroxide source such that the resulting bleached pulp comprises a pulp brightness of about 80% ISO or greater.
17. The method of claim 16, further comprising collecting a liquor and sending the liquor to a recovery boiler or a lignin recovery process.
18. The method of any one of claims 12-17, further comprising:
monitoring at least one of absorbance spectra of bleaching liquors, kappa number, fiber brightness, or fiber viscosity; and optimizing a bleaching sequence based upon the monitored values.
19. The method of claim 12, wherein the singlet oxygen source comprises a peracetate oxidant solution.
20. The method of claim 19, wherein the peracetate oxidant solution comprises peracetate anions and a peracid, wherein the peracetate oxidant solution has a pH from about 7 to about pH 12, and wherein the peracetate oxidant solution has a molar ratio of peracetate anions to peracid ranging from about 60:1 to about 6000:1
21. The method of claim 12, wherein the contacting the pulp with the singlet oxygen source preserves pulp viscosity.
22. A method of bleaching pulp, comprising:
contacting a pulp with a singlet oxygen source;
contacting the pulp with a chelating agent;
contacting the pulp with an alkaline peroxide source;
contacting the pulp with chlorine dioxide; and contacting the pulp with an alkaline peroxide source.
23. The method of claim 22, further comprising:
monitoring at least one of absorbance spectra of bleaching liquors, kappa number, fiber brightness, or fiber viscosity; and optimizing a bleaching sequence based upon the monitored values.
24. The method of claim 22, wherein the singlet oxygen source comprises a peracetate oxidant solution.
25. The method of claim 24, wherein the peracetate oxidant solution comprises peracetate anions and a peracid, wherein the peracetate oxidant solution has a pH from about 7 to about pH 12, and wherein the peracetate oxidant solution has a molar ratio of peracetate anions to peracid ranging from about 60:1 to about 6000:1.
26. The method of claim 22, wherein the bleached pulp comprises a final brightness of at least 80% ISO.
27. A method of bleaching pulp, comprising contacting a pulp with a singlet oxygen source.
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Families Citing this family (33)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8317975B2 (en) * 2004-04-20 2012-11-27 The Research Foundation Of The State University Of New York Product and processes from an integrated forest biorefinery
BRPI0811530B1 (en) 2007-05-14 2019-01-02 Research Foundation Of State Univ Of New York composition comprising inducer (s) of physiological response to decanoic acid dispersion, surface, solution, ex vivo method of treating or inhibiting the formation of a biofilm on a surface
WO2012166997A2 (en) 2011-05-31 2012-12-06 Clean Chemistry, Llc Electrochemical reactor and process
US20170107128A1 (en) 2012-09-07 2017-04-20 Clean Chemistry, Inc. System and method for generation of reactive oxygen species and applications thereof
EP3066257B1 (en) * 2013-11-06 2019-03-06 Evonik Degussa GmbH Method for delignifying and bleaching pulp
EP3189016B1 (en) 2014-09-04 2020-06-03 Clean Chemistry, Inc. Method of water treatment utilizing a peracetate oxidant solution
GB2530987B (en) * 2014-10-03 2017-06-21 Nafici Env Res (Ner) Ltd A method for processing straw
WO2016154531A1 (en) 2015-03-26 2016-09-29 Clean Chemistry, Inc. Systems and methods of reducing a bacteria population in high hydrogen sulfide water
CA3007780C (en) 2015-12-07 2023-12-19 Clean Chemistry, Inc. Methods of pulp fiber treatment
US10883224B2 (en) 2015-12-07 2021-01-05 Clean Chemistry, Inc. Methods of pulp fiber treatment
US11136714B2 (en) 2016-07-25 2021-10-05 Clean Chemistry, Inc. Methods of optical brightening agent removal
MX2019015198A (en) 2017-06-15 2020-08-13 Evonik Operations Gmbh Antimicrobial treatment of animal carcasses and food products.
FI128324B (en) * 2017-06-21 2020-03-31 Kemira Oyj Method for manufacturing a fibrous web
US11231360B2 (en) * 2017-06-29 2022-01-25 Hydrite Chemical Co. Automatic titration device
US11311012B1 (en) 2017-09-07 2022-04-26 Clean Chemistry, Inc. Bacterial control in fermentation systems
US11001864B1 (en) 2017-09-07 2021-05-11 Clean Chemistry, Inc. Bacterial control in fermentation systems
CA3076370A1 (en) * 2017-09-25 2019-03-28 Ecolab Usa Inc. Use of medium chain peracids for biofilm inhibition in industrial recirculating water systems
US11192809B2 (en) * 2017-11-14 2021-12-07 Biosafe Systems Llc Chiller water sampling device
WO2019099623A1 (en) * 2017-11-16 2019-05-23 Peroxychem Llc Disinfection method for water and wastewater
US11619000B2 (en) * 2017-12-29 2023-04-04 Valmet Technologies Oy Method and a system for adjusting S/Na-balance of a pulp mill
US11472722B2 (en) 2018-03-01 2022-10-18 Spi Technology Ltd. Water energy matrix control
WO2019232385A1 (en) * 2018-05-31 2019-12-05 Peroxychem Llc Sporicidal methods and compositions
CN109970264B (en) * 2019-03-08 2021-09-17 中核通辽铀业有限责任公司 Method for controlling malodorous pollutants in evaporation pond of in-situ leaching uranium mining mine
US11602896B2 (en) * 2019-08-14 2023-03-14 Mighty Buildings, Inc. 3D printing of a composite material via sequential dual-curing polymerization
EP4030914A4 (en) 2019-09-20 2022-10-12 Chemtreat, Inc. Sanitary food washing stage in food production
EP3797592A1 (en) 2019-09-25 2021-03-31 Sani-Marc Inc. Peracetic compositions, methods and kits for removing biofilms from an enclosed surface
CN112211028A (en) * 2020-09-18 2021-01-12 滁州兴邦聚合彩纤有限公司 Preparation method of chemical fiber pulp
CN114689722A (en) * 2020-12-31 2022-07-01 深圳市海普瑞药业集团股份有限公司 Method for detecting content of glycosaminoglycan carboxylated derivatives in sample and application of method
US11649398B1 (en) 2021-12-09 2023-05-16 Saudi Arabian Oil Company Composition and method of using date palm fibers in hydraulic fracturing
TWI799284B (en) * 2022-06-06 2023-04-11 友達光電股份有限公司 The system and method for water quality estimating and sterilization controlling
US20240003861A1 (en) * 2022-06-30 2024-01-04 Saudi Arabian Oil Company Automated method and system to measure residual biocide in seawater
SE546053C2 (en) * 2022-09-27 2024-04-30 Stora Enso Oyj A method for reducing the load of microbial contaminants in a pulp stock comprising a recycled fiber fraction
CN115787332A (en) * 2022-11-11 2023-03-14 玖龙纸业(东莞)有限公司 Method for controlling peculiar smell of paper

Family Cites Families (96)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3719552A (en) 1971-06-18 1973-03-06 American Cyanamid Co Bleaching of lignocellulosic materials with oxygen in the presence of a peroxide
AT326611B (en) 1972-07-31 1975-12-29 Henkel & Cie Gmbh BLEACHING AID SUITABLE AS A COMPONENT OF POWDERED DETERGENTS AND BLEACHING AGENTS
US4055505A (en) 1974-07-12 1977-10-25 Colgate-Palmolive Company Activated percompound bleaching compositions
US4076621A (en) 1976-03-15 1978-02-28 Air Resources, Inc. Chelate oxidation of hydrogen sulfide in sour water
SE415580C (en) 1977-05-11 1984-10-15 Mo Och Domsjoe Ab PROCEDURE FOR REGULATING THE SUPPLY OF REACTIONAL CHEMICALS BY DELIGNIFICATION OF CELLULOSAMENTAL
US4393037A (en) 1981-12-16 1983-07-12 Union Oil Company Of California Method for reconditioning bacteria-contaminated hydrogen sulfide removing systems
FR2552125B1 (en) 1983-09-16 1986-03-21 Interox PROCESS FOR THE TREATMENT OF CELLULOSIC MATERIALS BY OXIDIZING AGENTS
US4722773A (en) 1984-10-17 1988-02-02 The Dow Chemical Company Electrochemical cell having gas pressurized contact between laminar, gas diffusion electrode and current collector
US4673473A (en) 1985-06-06 1987-06-16 Peter G. Pa Ang Means and method for reducing carbon dioxide to a product
SE455822B (en) 1985-12-03 1988-08-08 Mo Och Domsjoe Ab PROCEDURE TO META THE CHEMICALS CONTENT IN CELLULOSAMAS INDUSTRY AND APPARATUS FOR IMPLEMENTATION OF THE PROCEDURE
US4872953A (en) 1986-12-18 1989-10-10 Eze Products, Inc. Apparatus for improving the quality of paper manufactured from recycled paper with a hydrokinetic amplifier
DK71987D0 (en) 1987-02-13 1987-02-13 Nordiske Kabel Traad PROCEDURE FOR CLEANING OIL AND CHEMICAL POLLUTANTS
DE3816989A1 (en) 1987-08-05 1989-02-16 Peroxid Chemie Gmbh DETERMINATION OF CLEANING SLUDGE
US5246543A (en) * 1989-08-18 1993-09-21 Degussa Corporation Process for bleaching and delignification of lignocellulosic materials
CA2053035C (en) * 1990-10-12 1997-09-30 Repap Enterprises Inc. Chlorine-free wood pulps and process of making
ATE132926T1 (en) 1992-07-06 1996-01-15 Solvay Interox METHOD FOR DELIGNIFICATION OF CHEMICAL PULP
DE651730T1 (en) 1992-07-23 1996-03-14 Diversey Corp., Mississauga, Ontario METHOD AND DEVICE FOR MONITORING MICROORGANISMS.
JP2864167B2 (en) 1992-11-27 1999-03-03 エカ ノーベル アクチェボラーグ Delignification method of pulp containing lignocellulose.
US6007678A (en) 1992-11-27 1999-12-28 Eka Nobel Ab Process for delignification of lignocellulose-containing pulp with an organic peracid or salts thereof
US5387317A (en) 1993-01-28 1995-02-07 The Mead Corporation Oxygen/ozone/peracetic aicd delignification and bleaching of cellulosic pulps
US5683724A (en) * 1993-03-17 1997-11-04 Ecolab Inc. Automated process for inhibition of microbial growth in aqueous food transport or process streams
US6183623B1 (en) 1993-07-13 2001-02-06 Lynntech, Inc. Electrochemical conversion of anhydrous hydrogen halide to halogen gas using an ionically conducting membrane
CA2129489C (en) 1993-08-05 2000-10-10 Judy G. Lazonby Method and composition for inhibiting growth of microorganisms including peracetic acid and a non-oxidizing biocide
US5472619A (en) 1993-09-03 1995-12-05 Birko Corporation Waste water treatment with peracetic acid compositions
SE502172C2 (en) 1993-12-15 1995-09-04 Mo Och Domsjoe Ab Process for the preparation of bleached cellulose pulp with a chlorine-free bleaching sequence in the presence of carbonate
US5565073A (en) 1994-07-15 1996-10-15 Fraser; Mark E. Electrochemical peroxide generator
US5624575A (en) * 1995-04-28 1997-04-29 Nalco Chemical Company Method for preventing microbial deposits in the papermaking process with ethylene oxide/propylene oxide copolymers
CN1055737C (en) 1996-01-15 2000-08-23 南京林业大学 Prescription and process for intensively bleaching pulp using singlet state oxygen in alkali bleaching stage of multi-stage process
IT1282367B1 (en) 1996-01-19 1998-03-20 De Nora Spa IMPROVED METHOD FOR THE ELECTROLYSIS OF WATER SOLUTIONS OF HYDROCHLORIC ACID
DE19614587A1 (en) * 1996-04-13 1997-10-16 Jaschinski Thomas Dipl Holzw Process and bleaching solution for bleaching cellulosic fibers
US5817240A (en) 1996-11-12 1998-10-06 The University Of Akron Catalytic fixed bed reactor systems for the destruction of contaminants in water by hydrogen peroxide
FI112958B (en) 1997-12-19 2004-02-13 Kemira Oyj Method for bleaching chemical pulp and use of bleaching solution
US6015536A (en) 1998-01-14 2000-01-18 Ecolab Inc. Peroxyacid compound use in odor reduction
FR2776312B1 (en) 1998-03-18 2000-05-05 Air Liquide PROCESS FOR DESTRUCTION OF FLUORESCENT AGENTS CONTAINED IN OLD PAPER BY PERACETIC ACID
ATE252175T1 (en) 1998-04-17 2003-11-15 Alberta Res Council METHOD FOR PRODUCING LIGNOCELLULOSE-CONTAINING PULP FROM NON-WOODY MATERIAL
US7335246B2 (en) 1998-05-14 2008-02-26 United States Of America Enviromental Protection Agency Contaminant adsorption and oxidation via the fenton reaction
US6569286B1 (en) * 1998-09-30 2003-05-27 Warwick International Group Limited Method for the alkaline bleaching of pulp with a peroxyacid based oxygen bleaching species using an agglomerated bleach activator
WO2000069778A1 (en) * 1999-05-17 2000-11-23 Buckman Laboratories International, Inc. Methods of using percarboxylic acid or anions thereof and methods of making the same
US6294047B1 (en) 1999-07-30 2001-09-25 Institute Of Paper Methods for reducing fluorescence in paper-containing samples
MXPA02001162A (en) 1999-08-05 2004-05-21 Steris Inc Electrolytic synthesis of peracetic acid.
US6562225B2 (en) 1999-08-30 2003-05-13 The Boeing Company Chemical oxygen-iodine laser with electrochemical regeneration of basic hydrogen peroxide and chlorine
US20010050234A1 (en) 1999-12-22 2001-12-13 Shiepe Jason K. Electrochemical cell system
JP2002317287A (en) 2001-04-18 2002-10-31 Permelec Electrode Ltd Electrolytic cell for preparation of hydrogen peroxide and method for producing hydrogen peroxide
DE60210085T2 (en) 2001-06-29 2006-11-09 The Procter & Gamble Company, Cincinnati STABILITY-RESISTANT PERSONALIZATION SYSTEM SUITABLE FOR TISSUE TREATMENT
US6712949B2 (en) 2001-07-22 2004-03-30 The Electrosynthesis Company, Inc. Electrochemical synthesis of hydrogen peroxide
US7008545B2 (en) * 2002-08-22 2006-03-07 Hercules Incorporated Synergistic biocidal mixtures
US20040112555A1 (en) 2002-12-03 2004-06-17 Jeffrey Tolan Bleaching stage using xylanase with hydrogen peroxide, peracids, or a combination thereof
US20040200588A1 (en) 2003-04-10 2004-10-14 Walker Jayne M.A. Method of controlling microorganisms in hydrogen peroxide pulp bleaching processes
GB0328124D0 (en) 2003-12-04 2004-01-07 Daly James Membrane electrolyser with a two part end design
US7614439B2 (en) * 2004-10-05 2009-11-10 Stephen Lukos Roller tube having external slot for mounting sheet material
WO2006099029A2 (en) 2005-03-11 2006-09-21 Board Of Supervisors Of Louisiana State University And Agricultural And Mechanical College Chemical oxidation for cellulose separation
US8562222B2 (en) 2005-06-24 2013-10-22 Seagate Technology Llc Hub and spindle assembly
WO2007008591A2 (en) 2005-07-07 2007-01-18 Applied Intellectual Capital Methods and apparatus for generating oxidizing agents
CN101147286A (en) 2005-08-25 2008-03-19 松下电器产业株式会社 Electrode for use in oxygen reduction
WO2007087345A2 (en) 2006-01-25 2007-08-02 The Administrators Of The Tulane Educational Fund Oxidative treatment method
JP2007242433A (en) 2006-03-09 2007-09-20 Permelec Electrode Ltd Electrode catalyst for electrochemical reaction, manufacturing method of the same, and electrochemical electrode having the same
US9056784B2 (en) 2006-09-19 2015-06-16 Ken V. Pandya High efficiency water-softening process
US7754064B2 (en) * 2006-09-29 2010-07-13 Eltron Research & Development Methods and apparatus for the on-site production of hydrogen peroxide
FI119800B (en) * 2006-11-09 2009-03-31 Kemira Oyj Procedures for preventing the growth of microorganisms and combinations that prevent the growth of microorganisms
US8999173B2 (en) 2007-06-04 2015-04-07 Global Water Holdings, Llc Aqueous treatment apparatus utilizing precursor materials and ultrasonics to generate customized oxidation-reduction-reactant chemistry environments in electrochemical cells and/or similar devices
US7763768B2 (en) 2007-07-05 2010-07-27 King Saud University Method for the preparation of reactive hydrogen peroxide in deep eutectic solvents
US20090090478A1 (en) 2007-10-05 2009-04-09 Hollomon Martha G Selectivity improvement in oxygen delignification and bleaching of lignocellulose pulp using singlet oxygen
WO2010005607A2 (en) 2008-03-19 2010-01-14 Eltron Research & Development, Inc. Production of peroxycarboxylic acids
JP5230242B2 (en) * 2008-04-09 2013-07-10 三菱重工環境・化学エンジニアリング株式会社 Method and system for methane fermentation treatment of food waste
DE112009000921B4 (en) 2008-04-14 2015-12-17 Mitsubishi Electric Corp. Active oxygen generating device and its use
US7655213B2 (en) 2008-05-13 2010-02-02 General Electric Company Direct oxidation of sulfur with carbon dioxide recycle
FR2932952A1 (en) 2008-06-26 2010-01-01 Orbeco Inc AQUEOUS COMPOSITION, IN PARTICULAR DISINFECTANT, BASED ON H202 MANUFACTURING METHOD AND USE.
US20100078331A1 (en) 2008-10-01 2010-04-01 Scherson Daniel A ELECTROLYTIC DEVICE FOR GENERATION OF pH-CONTROLLED HYPOHALOUS ACID AQUEOUS SOLUTIONS FOR DISINFECTANT APPLICATIONS
US20100179368A1 (en) 2008-11-07 2010-07-15 Aries Associates, Inc. Novel Chemistries, Solutions, and Dispersal Systems for Decontamination of Chemical and Biological Systems
WO2010059459A1 (en) 2008-11-20 2010-05-27 Aries Associates, Inc. Novel chemistries, solutions, and dispersal systems for decontamination of chemical and biological systems
US20100176066A1 (en) 2008-12-09 2010-07-15 Peragen Systems Inc. Method of Improving Efficiency of UV Photolysis of Peracetic Acid for Disinfection and Organic Destruction
WO2010080274A2 (en) 2008-12-18 2010-07-15 Fmc Corporation Peracetic acid oil-field biocide and method
IT1396051B1 (en) 2009-09-28 2012-11-09 Montemurro PROCEDURE FOR MINIMIZING SITE OF PURIFICATION OF WASTE AND OTHER WASTE.
AU2011229776B2 (en) 2010-03-23 2013-11-28 International Paper Company Improved BCTMP filtrate recycling system and method
US8845860B2 (en) * 2010-09-16 2014-09-30 Georgia-Pacific Consumer Products Lp High brightness pulps from lignin rich waste papers
US20120322873A1 (en) 2010-12-28 2012-12-20 Nalco Company Use of a buffer with a biocide precursor
US8454838B2 (en) 2011-03-30 2013-06-04 Crystal Lagoons (Curacao) B.V. Method and system for the sustainable cooling of industrial processes
US20120267315A1 (en) 2011-04-20 2012-10-25 Soane Energy, Llc Treatment of wastewater
WO2012166997A2 (en) 2011-05-31 2012-12-06 Clean Chemistry, Llc Electrochemical reactor and process
AR087707A1 (en) 2011-08-30 2014-04-09 Cargill Inc ARTICLES MANUFACTURED FROM A PULP COMPOSITION
JP5285197B1 (en) 2011-09-30 2013-09-11 日本製紙株式会社 Method for producing cellulose nanofiber
AR094422A1 (en) 2011-10-25 2015-08-05 Basf Se SUSPENSION CONCENTRATION
WO2013064484A1 (en) 2011-11-01 2013-05-10 Kemira Oyj Method of treating oily waters
CN104254496B (en) * 2012-03-30 2016-10-26 艺康美国股份有限公司 Peracetic acid/hydrogen peroxide and peroxide reducing agent are for processing drilling fluid, fracturing fluid, recirculation water and the purposes of discharge water
US9719179B2 (en) 2012-05-23 2017-08-01 High Sierra Energy, LP System and method for treatment of produced waters
WO2014100828A1 (en) 2012-12-21 2014-06-26 Liquid Light, Inc. Method and system for production of oxalic acid and oxalic acid reduction products
US20170107128A1 (en) 2012-09-07 2017-04-20 Clean Chemistry, Inc. System and method for generation of reactive oxygen species and applications thereof
US10281383B2 (en) 2012-11-15 2019-05-07 Solenis Technologies, L.P. System and methods of determining liquid phase turbidity of multiphase wastewater
EP2754644A1 (en) * 2013-01-15 2014-07-16 Voltea B.V. Evaporative recirculation cooling water system, method of operating an evaporative recirculation cooling water system and a method of operating a water deionizing system
US9670080B2 (en) 2013-06-24 2017-06-06 Baker Hughes Incorporated Composition and method for treating oilfield water
EP3189016B1 (en) 2014-09-04 2020-06-03 Clean Chemistry, Inc. Method of water treatment utilizing a peracetate oxidant solution
WO2016154531A1 (en) 2015-03-26 2016-09-29 Clean Chemistry, Inc. Systems and methods of reducing a bacteria population in high hydrogen sulfide water
CA3007780C (en) 2015-12-07 2023-12-19 Clean Chemistry, Inc. Methods of pulp fiber treatment
US10883224B2 (en) 2015-12-07 2021-01-05 Clean Chemistry, Inc. Methods of pulp fiber treatment
US11136714B2 (en) 2016-07-25 2021-10-05 Clean Chemistry, Inc. Methods of optical brightening agent removal
US11001864B1 (en) 2017-09-07 2021-05-11 Clean Chemistry, Inc. Bacterial control in fermentation systems

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